Perovskite catalyst system for lean burn engines

ABSTRACT

A catalyst system for use with an internal combustion engine to provide emissions reductions under lean and stoichiometric operating conditions. The catalyst system comprises a first catalyst comprised of a newly developed Perovskite-based formulation having an ABO 3  crystal structure designed to bring the precious metal and NOx trapping elements close together. The first catalyst acts primarily to maximize the reduction of emissions under lean operating conditions. The catalyst system also comprises a second catalyst comprised of precious metals which acts primarily to maximize the reduction of emissions under stoichiometric conditions.

BACKGROUND OF INVENTION

1. Field of the Invention

The present invention is directed to a catalyst system for use withinternal combustion engines to oxidize hydrocarbons, carbon monoxide andreduce nitrogen oxides in an exhaust gas when the engine is operated atboth lean and stoichiometric air/fuel ratios. More particularly, thecatalyst system of this invention includes two catalysts. The firstcatalyst is designed specifically to optimize the reduction of noxiousemissions under lean conditions. This first catalyst includes a newPerovskite-based formulation designed to achieve close proximity betweenprecious metal and NOx binding elements.

The second catalyst is designed specifically to maximize the reductionof HC, CO and NOx under stoichiometric operations and to treat anybreakthrough NOx emissions from the first catalyst. This second catalystcontains precious metals and may optionally include BaO.

2. Background Art

Catalysts have long been used in the exhaust systems of automotivevehicles to convert carbon monoxide, hydrocarbons, and nitrogen oxides(NOx) produced during engine operation into nonpolluting gases includingcarbon dioxide, water and nitrogen. When a gasoline-powered engine isoperated at a stoichiometric or slightly rich air/fuel ratio, i.e.,between about 14.6 and 14.4, catalysts containing precious metals likeplatinum, palladium and rhodium are able to efficiently convert allthree gases simultaneously. Typically, such catalysts use a relativelyhigh loading of precious metal to achieve the high conversion efficiencyrequired to meet the stringent emission standards of many countries.Because of the high cost of the precious metals, these catalysts areexpensive to manufacture.

To improve vehicle fuel efficiency and lower CO₂ emissions, it ispreferable to operate an engine under lean conditions. Lean conditionsare air/fuel mixtures greater than the stoichiometric mixture (anair/fuel mixture of 14.6), typically air/fuel mixtures greater than 15.While lean operation improves fuel economy, operating under leanconditions increases the difficulty in treating some polluting gases,especially NOx.

For some catalysts, if the air/fuel ratio is lean even by a smallamount, NOx conversion is significantly reduced. One way to provideair/fuel control is through the use of a HEGO (Heated Exhaust GasOxygen) sensor to provide feedback to the control systems. HEGO sensors,however, over time develop a lean bias as a result of poisoning.Accordingly, even with a HEGO sensor it is important to have a catalystthat can maximize the reduction of NOx emission under lean conditions.

To maximize NOx reduction under lean operating conditions, a lean NOxtrap is often used. The inclusion of a NOx trap enhances the reductionof NOx while the engine is operated under lean conditions. The NOx trapfunctions in a cyclic manner. When the NOx trap reaches the effectivestorage limit, the engine is operated under normal or rich conditions topurge the NOx trap. After the NOx trap has been purged, the engine canreturn to lean operation.

However, in addition to problems associated with thermal stability andsulfur tolerance, lean NOx traps (LNT) have the following two knownproblems: (1) a problem referred to as “NOx breakthrough”, thebreakthrough of NOx during the NOx trap transition from the lean to therich cycle; and (2) a reduction in fuel economy that results fromfrequent purges during the rich cycle. Test results depicted in FIG. 2shows this NOx breakthrough for LNTs with different oxygen storagecapacity (OSC). This total NOx breakthrough has been found to be greaterthan 73% of the total NOx emitted during the operation of a lean NOxtrap.

FIG. 2 also shows the effects of oxygen storage capacity on NOxbreakthrough of a lean NOx trap during the lean-to-rich transition. LNTL, which has the highest OSC, results in the largest amount of NOxbreakthrough, while the lower the OSC (from LNT M down to LNT N), thelower the amount of NOx breakthrough. It is believed that NOxbreakthrough during the lean-rich transition occurs due to theexothermic heat generated from the oxidation of reductants, CO, HC andH₂, by the oxygen released from the oxygen storage material (see FIG.2)—the temperature rise can be as high as 80–100° C.

With regard to the fuel economy penalty, this is believed to be theresult of high oxygen storage capacity of the lean NOx trap, low NOxtrapping capacity, and/or high exhaust flow rate. The OSC requiresadditional reductants (i.e., fuel) to reduce the oxygen storagematerials during each lean-to-rich transition, while the low NOxtrapping capacity requires that the frequency of purges be increased.

The present invention avoids the cost and complexity of the NOx trap andthe reduced fuel economy from frequent NOx trap purging bysystematically reducing the amount of NOx during engine operation, evenunder lean conditions.

To solve the above problems, the present invention provides a newcatalyst system comprising two catalysts that can treat all exhaustemissions, CO, HC and NOx under both stoichiometric and lean conditions.In particular, the forward catalyst uses a newly developedPerovskite-based formulation which achieves the requisite closeproximity between precious metal and NOx binding elements.

The closest known prior art includes modified three-way catalysts. Forexample, U.S. Pat. No. 4,024,706, incorporated herein by reference,teaches a method of enlarging the air/fuel ratio over which a catalystoperates by including an oxygen storage material. The method involvescontrolling the air/fuel ratio of the fuel mixture being burned by theengine such that the ratio is transferred into equal amounts going tothe rich and lean side of a stoichiometric condition as previouslydescribed. The use of an oxygen storage material, however, is believedto result in NOx breakthrough, which increases NOx emissions rather thanreducing them.

U.S. Pat. No. 5,977,017 teaches a Perovskite-type catalyst that consistsmainly of a metal oxide composition. The metal oxide composition isrepresented by the general formula:A_(a-x)B_(x)MO_(b),where

A is a mixture of elements originally in the form of a single phasemixed lanthanides collected from bastnasite;

B is a divalent or monovalent cation;

M is at least one element selected from the group consisting of elementsof an atomic number from 22–30, 40–51, and 73–80;

a is 1 or 2;

b is 3 when a is 1 or b is 4 when a is 2; and

x is between 0 and 0.7.

This general Perovskite structure, however, is not designed to maximizeNOx storing and releasing functions—by providing the requisite closeproximity between the precious metal and the NOx-binding element. Incontrast, the newly developed Perovskite structure of this invention isspecifically designed to maximize NOx storage and release.

U.S. Pat. No. 4,321,250 also teaches a Perovskite-type catalyst having aABO₃ crystal structure with about 1 to 20 percent of the B cation sitesoccupied by Rh ions and the remainder of the B cation sites occupied byions consisting essentially of cobalt and the A cation sites occupied bylanthanide ions of atomic number 57 to 71 and ions of at least one metalof groups IA, IIA or IVA of the period table having an ionic radii ofabout 0.9 A to 1.65 A and proportioned so that no more than 50 percentof the cobalt ions are tetravalent and the remaining cobalt ions aretrivalent. This composition generally represents Perovskite catalyststhat were useful to produce hydrogen in steam reformers.

The use of such types of Perovskite catalysts as an automotive catalystor their use in combination with other catalysts to produce a NOxtolerant catalyst was not known prior to this invention.

SUMMARY OF INVENTION

The present invention is directed to a catalyst system for use with aninternal combustion engine. In broad terms, the catalyst system of thisinvention is designed specifically to maximize reduction of NOxemissions during lean exhaust conditions. The catalyst system can be asingle catalyst or a combination of two or more catalysts. Whether onecatalyst is used or more than one, the catalyst system is designed tomaximize reduction of NOx emissions under lean conditions, and maximizethe reduction of HC, NOx and CO emissions under stoichiometricconditions.

More specifically, this invention relates to a new Perovskiteformulation for a catalyst to be used in a catalyst system thatmaximizes the reduction of HC, CO, and NOx under both stoichiometric andlean operating conditions. This new Perovskite-based formulation is tobe used in the forward catalyst of a catalyst system, which also uses adownstream catalyst, wherein the forward catalyst is used primarily toreduce emissions under lean operating conditions, and wherein thedownstream catalyst is designed primarily to reduce emissions understoichiometric conditions. It is believed that the newly designedPerovskite-based forward catalyst is optimized for reducing emissionsunder lean operating conditions by achieving close proximity between theprecious metal and NOx-binding elements, such as barium, magnesium andpotassium.

We have found that a catalyst system of this construction andcomposition is capable of oxidizing hydrocarbons and carbon monoxidewhile also reducing NOx during systematic operation under leanconditions. Accordingly, this invention provides combined treatment ofemissions of engines operated under both stoichiometric conditions andlean burn conditions, and provides excellent thermal stability and theresulting metal dispersion eliminates NOx breakthrough during the leanto rich transition. This and other aspects of the invention will bedescribed in detail below.

BRIEF DESCRIPTION OF DRAWINGS

FIG. 1 is a graph of engine speed versus brake mean effective pressure(BMEP) at different air/fuel ratios for typical internal combustionengines and the proposed new stratified-charged engine;

FIG. 2 is a graph of NOx released during the transition from lean-richoperation in milliseconds for three lean NOx traps with different oxygenstorage capacities (OSC) in a flow reactor at 350° C.;

FIG. 3 is a schematic view of a catalyst system that incorporates thepresent invention, showing two catalysts and an EGO sensor positionedtherebetween to maximize the treatment of emissions both understoichiometric operation and under stratified-charged lean conditions;

FIG. 4 is a schematic diagram of the Perovskite crystal structure;

FIG. 5 a shows the NOx trapping efficiency of the catalyst as preparedin Example 1; and

FIG. 5 b shows the conversion efficiency of the catalyst as prepared inExample 1.

DETAILED DESCRIPTION

Demands for improved fuel economy and lower CO₂ emissions haveencouraged engine manufacturers to increase the air/fuel ratio above14.7—above stoichiometric conditions.

In one newer engine design, the engine is run under stoichiometricconditions most of the time, except under low load (brake mean effectivepressure (BMEP)<1.2 bar), low engine speed (RPM<1750) conditions, whenthe engine is run under stratified-charged lean conditions, an air/fuelratio of approximately 30. The operation diagram of a stratified charged(SC) engine is schematically shown as FIG. 1. FIG. 1 depicts theoperation regions of typical internal combustion engines, homogeneouslycharged engines, with an air/fuel ratio=28, an engine operating understoichiometric conditions, an air/fuel ratio of 14.6 and an engineoperating at full load λ<1, wherein λ is the air/fuel excess ratio. Itis predicted that this engine operation would increase fuel economy byapproximately 5%. For such engines, designed to operate at leastpartially under lean conditions, the present invention provides acatalyst system capable of reducing CO, HC, and NOx—in line with currentand future emission standards.

As seen in FIG. 3, under this invention, one embodiment of the catalystsystem 10 includes two closely-coupled catalysts—a forward catalyst 12to maximize the reduction of engine 16 emissions under lean conditionsand a downstream catalyst 14 to maximize the reduction of emissionsunder stoichiometric conditions. In particular, the forward catalyst 12of this invention is comprised of a newly developed Perovskitecomposition designed to increase proximity between the precious metaland the NOx binding metals and to eliminate the oxygen storage capacity.

In general, Perovskites have the generic formula ABO₃. Perovskites canbe classified into three categories according to the valence of the Aand B elements: A₁B₅O₃, A₂B₄O₃, and A₃B₃O₃. A schematic crystalstructure of a Perovskite, CaTiO₃, is shown in FIG. 4. As can be seen inFIG. 4, the B element is at the octahedral interstitial site at thecenter of the unit cell. As a result, B generally has a smaller ionicradius than A. In fact, an empirical tolerance factor defines therelationship between the ionic radius of A and the ionic radius of B:T=(r_(A)+r_(O))/1.4144 (r_(B)+r_(O)), T must satisfy 0.75 less than Tless than 1.00.

The active sites for a Perovskite are normally the B sites. For areaction NO+CO to occur, the site should have balanced oxidation andreduction activity. Too strong an oxidation activity will drive COimmediately to CO₂ without involving NO, and too strong a reductionactivity will drive NO to NOC or N₂O without converting CO to CO₂. Wehave found that cobalt, Co, has this balanced oxidation/reductionproperty, and thus be placed on the B site. We have also found thatlanthanum, La, at the A site provides adequate stability for thePerovskite. As a result, in this invention, the preferred parentPerovskite structure is LaCoO₃.

For NOx storing and releasing to occur, high capacity, fast storing andreleasing kinetics is further required. This is accomplished bysubstituting barium, Ba, to the lanthanum, La, (A) sites to formLa_(1 x)Ba_(x)CoO₃. Since lanthanum is trivalent while barium isdivalent, the charge balance of the crystal structure results in theformation of either a tetravalent cobalt or positive holes (oxygenvacancies):

$\begin{matrix}{{La}_{1 - x}^{3\; t}B\; a_{x}^{2\; t}{Co}_{1 - x}^{3\; t}{Co}_{x}^{4\; t}O_{3}} \\{{La}_{1 - x}^{3\; t}B\; a_{x}^{2\; t}{Co}^{3\; t}O_{3 - {x/2}}{VO}_{x/2}}\end{matrix}$

By substituting barium with lanthanum, the oxygen vacancies createdprovide space for bulk nitrate or nitrite formation, to achieve NOxstorage, and also accelerate the diffusion of nitrogen atoms inside thePerovskite structure.

For this invention, part of the lanthanum at the A site can also besubstituted with magnesium, Mg, and potassium, K, to provide balancedtrapping function at both low and high temperatures. Additionally, thelanthanum at the A site can be substituted with Sr.

In a preferred embodiment, the parent Perovskite structure LaCoO₃ can bemodified, wherein cobalt is substituted at the B site with preciousmetals such as platinum and rhodium, or a transition metal such as iron,copper, and manganese—to increase the activity and selectivity of thePerovskite structure. The substituted metal, i.e., platinum, will thushave close proximity with barium at the molecular level which improvesthe thermal stability and NOx reducing capabilities of the forwardcatalyst 12, as shown in FIG. 3.

This newly developed Perovskite catalyst composition can generally beprepared according to a sol-gel method. The Perovskite composition canbe coated onto a block of honeycomb cordierite substrate (600 csi).After the Perovskite is coated, extra platinum and rhodium can then beimpregnated onto the coated substrate in a ratio of 7:1. The platinumand rhodium are loaded at approximately 20–100 g/ft³.

In one preferred embodiment, the Perovskite used as the forward catalysthas a formula of: La_(0.5)Ba_(0.5)Co_(0.9)Pt_(0.1)O₃. This preferredPerovskite composition can be prepared using a solution of citric acidand ethylene glycol. More specifically, 0.667 gm of citric acid and 4cm³ of ethylene glycol per 1 gm of the final oxide mixture was added toa boiling solution of La, Ba, Co nitrates and tetra-amine platinumnitrate in the desired ratios. The resulting mixture is evaporated withvigorous stirring until formation of a gel, then further evaporated on ahot plate to remove the residual liquid. The resulting powder was groundand heated up to 300° C. for six hours, to remove the organic matter andthen ground again and calcined at 900° C. for 30 hours in air.

Another preferred Perovskite composition has the formula:La_(0.5)Ba_(0.5)Co_(0.9)Rh_(0.1)O₃

Yet another preferred Perovskite composition has the formula:La_(0.5)Ba_(0.5)Co_(0.6)Fe_(0.3)Pt_(0.1)O₃

It should be noted that the above Perovskite structures can also beprepared using the co-precipitation method. Co-precipitation techniquesare well known to those skilled in the art. According to suchtechniques, the soluble salts can be dissolved in a solvent, forexample, nitrates of the metals are dissolved in water. Co-precipitationis then obtained by making the solution basic, e.g., a pH of 9 by addinga base like ammonium hydroxide. Other soluble metal compounds such as,for example, sulfates and chlorides, may be used as may mixtures orvarious soluble compounds, e.g., nitrates with chlorides. Theprecipitate would then be heated to decompose it to the mixed metaloxide. This heating and calcination can be carried out at temperaturesof up to 900° C. It should be noted that the way in which the oxide isobtained for use in forming the catalyst is not critical to theinvention. Still other ways and other soluble salts would be apparent tothose skilled in the art in view of the present disclosure.

As is known in the art, for useful application of the catalyst in anexhaust gas system, the catalyst is deposited or washcoated on asubstrate (mechanical carrier) made of a high temperature stable,electrically insulating material such as cordierite, mullite, etc. Amechanical carrier is preferably comprised of a monolithic magnesiumaluminum silicate structure, i.e., cordierite, although theconfiguration is not critical to the catalyst of this invention.

It is preferred that the surface area of the monolithic structureprovide 50–1000 meters square per liter structure, as measured bynitrogen adsorption. Cell density should be maximized consistent withpressure drop limitations and is preferable in the range of 200–800cells per square inch of cross-sectional area of the structure. Thesubstrate may be in any suitable configuration, often being employed asa monolithic honeycomb structure, spun fibers, corrugated configurationsuseful in this invention and suitable in an exhaust gas system will beapparent to those skilled in the art in view of the present disclosure.

Techniques for providing an oxide washcoat on a substrate are well knownto those skilled in the art. Generally, a slurry of the mixed metaloxide particles and optionally stabilizer particles are coated on asubstrate, e.g., added by dipping or spraying, after which the excess isgenerally blown off. After the slurry of mixed metal oxide particles arecoated on the substrate, the substrate is heated to dry and calcine thecoating, generally at a temperature of about 700° C. for about 2–3hours. Calcining serves to develop the integrity of the ceramicstructure of the washcoated oxide coating. The total amount of the oxidewashcoat carried on the substrate is about 10–40% (wt), based on theweight of the substrate coated. Several coatings of the substrate andthe washcoat may be necessary to develop the desired coatingthickness/weight on the substrate.

For the downstream catalyst 14 of FIG. 3, the basic formulation is acatalyst that can include excess Ba compounds to stabilize the aluminacarrier. Precious metals may also be provided on the calcined oxidecoating by any technique including the well-known wet impregnationtechnique from soluble precious metal precursor compounds. Water solublecompounds are preferred, including, but not limited to nitrate salts andmaterials for platinum like chloroplatinic acid. As is known in the art,after impregnating the washcoat with the precursor solution, it is driedand heated to decompose the precursor to its precious metal or preciousmetal oxide. As is known in the art, the precursor may initiallydecompose to the metal but be oxidized to its oxide in the presence ofoxygen. While some examples of precious metal precursors have beenmentioned above, they are not meant to be limiting. Still otherprecursor compounds would be apparent to those skilled in the art inview of the present disclosure.

In addition to this incorporation from a liquid phase, the preciousmetal, such as platinum, may be provided by sublimation of platinumchloride or other volatile platinum salts, by a solid state exchange inthe 300–500° C. temperature range using labile platinum compounds. Thereis no criticality to the type of precursor compounds that may be used toprovide the precious metal according to this invention.

FIG. 3 depicts one embodiment of the catalyst system 10 of the presentinvention. As shown, the catalyst system 10 includes two catalysts 12,14 in a close-coupled location. The forward catalyst 12 is optimized tofunction when the engine 16 is operated under lean conditions. Theforward catalyst 12 will store excess NOx during lean operation and thenrelease and convert the NOx when the engine 16 switches tostoichiometric or rich conditions. The downstream catalyst 14 isoptimized to effectively convert HC, CO, and NOx under stoichiometricoperations.

The forward catalyst 12 includes the newly developed Perovskitecomposite. By using this Perovskite composition, NOx emissions duringlean conditions are reduced. This reduction is believed to be the resultof the newly developed Perovskite composition which places the preciousmetal and NOx binding metals in close proximity.

The downstream catalyst 14 comprises a catalyst mixture PM-Rh, where PM(precious metal) is a catalyst material selected from the groupconsisting of platinum, palladium and combinations thereof and the PM isthen mixed with Rh (rhodium) to form the downstream catalyst 14 catalystmixture. This downstream catalyst 14 also preferably comprises analumina substrate, on which the PM-Rh catalyst mixture is coated.

In a preferred embodiment, the downstream catalyst 14 contains platinumand rhodium, in a ratio of Pt/Rh 9:1, and more preferably 7:1. The totalloading of the precious metal (PM) in the downstream catalyst 14 is,however, about 20–60 g/ft³, and more preferably 40–60 g/ft³, whichresults in a cost savings compared to these catalysts which have aprecious metal loading of approximately 100–120 g/ft³. In this preferredembodiment, both Pt and Rh are anchored on 2–20% (wt) high surface areaCe/Zr with high O₂ kinetics (e.g., Ce/Zr=50:50 molar ratio). The aluminawashcoat is preferably also stabilized by 2–20% BaO.

The foregoing catalyst system 10 eliminates the oxygen storage functionof the forward catalyst 12, which is normally present in lean NOx trapformulations, so that NOx breakthrough is minimized. The forwardcatalyst 12 can be purged and NOx converted when an engine controlmodule (ECM) senses that the engine is under high or low load,corresponding to acceleration or deceleration, respectively.

Optionally, an exhaust gas oxygen sensor 18 is positioned upstream ofthe downstream catalyst 14 between catalyst 12 and catalyst 14, as shownin FIG. 3. Under this arrangement, there is no fuel economy penalty fromthe offset of the oxygen storage capacity of the forward catalystbecause we have eliminated the oxygen storage capacity in the forwardcatalyst.

This catalyst system is expected to be used in automotive vehicles foremission treatment in the exhaust gas system where it functions tooxidize hydrocarbons, carbon monoxide, and simultaneously reducenitrogen oxides to desired emission levels.

One alternative embodiment of this invention uses just the Perovskiteforward catalyst 12 to reduce emissions from the exhaust streams of suchtwo-cylinder machines/devices as boats, jet skis, lawn mowers or cuttingdevices to provide a low cost catalyst. Under this embodiment, thePerovskite catalyst would be coated directly on the exhaust emittingcomponent of the device, i.e., a muffler, or alternatively coated on aninexpensive substrate, such as ceramic. To ensure that the catalystremains low cost, the cobalt B cation sites on the Perovskite crystalstructure would be substituted with a metal selected from the groupconsisting of iron, copper and manganese—not a precious metal. It shouldbe noted that for such Perovskite applications, low sulfur content fuelis preferred to avoid sulfur poisoning of the Perovskite catalyst.

EXAMPLE 1

La(NO₃)₃.6H₂O(108.25 g), Ba(NO₃)₂(65.34 g), Co(NO₃)₂.6H₂O (130.97 g),and Pt(NH₃)₄(NO₃)₂(19.35 g) are each added to 500 ml deionized water,heated to 100° C., and then mixed together to achieve a solution withthe final desired ratios. This stirred solution is heated and allowed toboil before adding a solution containing 0.667 g of citric acid and 4cm³ of ethylene glycol per 1 g of the final oxide mixture. The resultingmixture is evaporated with vigorous stirring until formation of a gel,and then further evaporated on a hot plate at 140° C. to remove theresidual liquid. The resulting powder is ground and heated to 300° C.for 6 hours and allowed to cool to room temperature. The powder isground again and then calcined in air at 900° C. for 30 hours. The finalpowder composition is La_(0.5)Ba_(0.5)Co_(0.9)Pt_(0.1)O₃.

EXAMPLE 2

The sample is prepared by the same method as described in Example 1 withthe exception of adding 16.25 g of Rh(NO₃)₃.2H₂O to 500 ml deionizedwater instead of Pt(NH₃)₄(NO₃)₂. The resulting powder isLa_(0.5)Ba_(0.5)Co_(0.9)Rh_(0.1)O₃.

EXAMPLE 3

La(NO₃)₃.6H₂O(108.25 g), Ba(NO₃)₂(65.34 g), Co(NO₃)₂.6H₂O (87.31 g),Fe(NO₃)₃.9H₂O(60.60 g), and Pt(NH₃)₄(NO₃)₂(19.35 g) are each added to500 ml deionized water, heated to 100° C., and then mixed together toachieve a solution with the final desired ratios. This stirred solutionis heated and allowed to boil before adding a solution containing 0.667g of citric acid and 4 cm³ of ethylene glycol per 1 gm of the finaloxide mixture. The resulting mixture is evaporated with vigorousstirring until formation of a gel, and then further evaporated on a hotplate at 140° C. to remove the residual liquid. The resulting powder isground and heated to 300° C. for 6 hours and allowed to cool to roomtemperature. The powder is ground again and then calcined in air at 900°C. for 30 hours. The final powder composition isLa_(0.5)Ba_(0.5)Co_(0.6)Fe_(0.3)Pt_(0.1)O₃.

The foregoing catalyst systems constructions and compositions have beenfound useful in reducing harmful engine emissions. Variations andmodifications of the present invention may be made without departingfrom the spirit and scope of the invention or the following claims.

1. A catalyst system for use in reducing emissions from an exhaust gasstream comprising: a first catalyst for optimizing the storage of NOxemissions under lean air/fuel ratios, comprising a Perovskite-type ABO₃crystal structure wherein the A cation sites are occupied by lanthanideions and the B cation sites are occupied by cobalt ions, wherein fromabout 1 to up to 70% of the lanthanide A cation sites are substitutedwith a NOx trapping metal selected from the group consisting of barium,magnesium, and potassium, wherein from about 1 to up to 60% of thecobalt B cation sites are substituted with a metal selected from thegroup consisting of platinum, rhodium, iron, copper and manganese; and asecond catalyst for optimizing the reduction of hydrocarbon, NOx and COemissions under stoichiometric air/fuel ratios, comprising a catalystmixture PM-Rh where PM is a catalyst material selected from the groupconsisting of platinum, palladium and combinations thereof, wherein thefirst and second catalysts are closely coupled, the first catalyst beingplaced in a forward position and the second catalyst being placed in adownstream position in the exhaust stream.
 2. The catalyst system ofclaim 1, wherein the first catalyst is prepared by sol-gel.
 3. Thecatalyst system of claim 1, wherein the first catalyst is prepared byco-precipitation.
 4. The catalyst system of claim 1, wherein the ratioof PM:Rh in the catalyst mixture PM-Rh is 9:1.
 5. The catalyst system ofclaim 1, wherein the ratio of PM:Rh in the catalyst mixture PM-Rh is7:1.
 6. The catalyst system of claim 1, wherein the PM has a totalloading of 20–60 g/ft³.
 7. The catalyst system of claim 1, wherein thePM has a total loading of 40–60 g/ft³.
 8. The catalyst system of claim1, wherein the first catalyst has the formulaLa_(0.5)Ba_(0.5)Co_(0.9)Rh_(0.1)O₃.
 9. The catalyst system of claim 1,wherein the first catalyst has the formulaLa_(0.5)Ba_(0.5)Co_(0.6)Fe_(0.3)Pt_(0.1)O₃.
 10. The catalyst system ofclaim 1, wherein the first catalyst has the formulaLa_(0.5)Ba_(0.5)Co_(0.9)Pt_(0.1)O₃.
 11. The catalyst system of claim 1,wherein the catalyst mixture PM-Rh is coated on an alumina substrate.12. The catalyst system of claim 11, wherein the alumina substrate inthe second catalyst is stabilized by 2–20% (wt) BaO.
 13. The catalystsystem of claim 11, wherein the PM is loaded on the alumina substrate bywet impregnation.
 14. The catalyst system of claim 1, wherein theplatinum and rhodium in the second catalyst are placed on Ce and Zrparticles of 2–20% (wt).
 15. The catalyst system of claim 1, wherein anexhaust gas sensor is placed between the first and second catalysts. 16.A catalyst system for use in reducing emissions from an exhaust gasstream of a device having an exhaust emitting component, comprising: acatalyst having a Perovskite-type ABO₃ crystal structure wherein the Acation sites are occupied by lanthanide ions and the B cation sites areoccupied by cobalt ions, wherein from about 1 to up to 70% of thelanthanide A cation sites are substituted with a NOx trapping metalselected from the group consisting of barium, magnesium, and potassium,wherein from about 1 to up to 60% of the cobalt B cation sites aresubstituted with a metal selected from the group consisting of iron,copper and manganese, the catalyst being positionable in a forwardposition in the exhaust relative to a second catalyst for optimizing thereduction of hydrocarbon, NOx and CO emissions under stoichiometricair/fuel ratios, the second catalyst comprising a catalyst mixture PM-Rhwhere PM is a catalyst material selected from the group consisting ofplatinum, palladium and combinations thereof.
 17. The catalyst system ofclaim 16, wherein the catalyst is coated on a ceramic substrate.
 18. Thecatalyst system of claim 16, wherein the catalyst is coated directlyonto the exhaust emitting component.
 19. A catalyst system for use inreducing emissions from an exhaust gas stream comprising: a firstcatalyst for optimizing the storage of NOx emissions under lean air/fuelratios, comprising a Perovskite-type ABO₃ crystal structure wherein theA cation sites are occupied by lanthanide ions and the B cation sitesare occupied by cobalt ions, wherein from about 1 to up to 70% of thelanthanide A cation sites are substituted with a NOx trapping metalselected from the group consisting of barium, magnesium, and potassium,wherein from about 1 to up to 60% of the cobalt B cation sites aresubstituted with a metal selected from the group consisting of platinum,rhodium, iron, copper and manganese; a second catalyst for optimizingthe reduction of hydrocarbon, NOx and CO emissions under stoichiometricair/fuel ratios, comprising a catalyst mixture PM-Rh where PM is acatalyst material selected from the group consisting of platinum,palladium and combinations thereof; and an exhaust gas sensor is placedbetween the first and second catalysts.